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CN102331462B - Method for measuring ammonia content in water-based adhesive for cigarettes - Google Patents

Method for measuring ammonia content in water-based adhesive for cigarettes Download PDF

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CN102331462B
CN102331462B CN 201110168337 CN201110168337A CN102331462B CN 102331462 B CN102331462 B CN 102331462B CN 201110168337 CN201110168337 CN 201110168337 CN 201110168337 A CN201110168337 A CN 201110168337A CN 102331462 B CN102331462 B CN 102331462B
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CN102331462A (en
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范多青
王庆华
史小波
李响丽
郭丽娟
杨艳萍
叶灵
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Hongyunhonghe Tobacco Group Co Ltd
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Abstract

本发明公开了一种测定烟用水基胶中氨含量的方法。烟用水基胶样品用盐酸水溶液振荡萃取,萃取液经离心、过滤后上离子色谱仪分析。同时配制不同浓度的NH4标准工作溶液并进行离子色谱仪分析。以外标法进行定量分析,并以氨的色谱峰面积与其相应的浓度进行回归分析,得到标准曲线,相关系数大于等于0.999,对制备的样品进行测定,测得样品中氨的峰面积,带入标准曲线,求得样品中氨的含量,由标准物质保留时间定性,由峰面积定量。本发明能有效检测烟用水基胶中氨的含量,操作快速、简单易行,采用梯度淋洗消除了各种离子尤其是钠离子的干扰,解决了烟用水基胶中氨含量的快速测定,填补了目前烟用水基胶氨测定的空白。

The invention discloses a method for measuring ammonia content in water-based glue for tobacco. Tobacco water-based rubber samples were extracted with hydrochloric acid aqueous solution, and the extract was centrifuged, filtered, and then analyzed by ion chromatography. At the same time, different concentrations of NH 4 standard working solutions were prepared and analyzed by ion chromatography. Quantitative analysis was carried out by the external standard method, and the regression analysis was carried out with the chromatographic peak area of ammonia and its corresponding concentration to obtain a standard curve, the correlation coefficient was greater than or equal to 0.999, and the prepared samples were measured to measure the peak area of ammonia in the sample. The standard curve is used to obtain the content of ammonia in the sample, which is qualitatively determined by the retention time of the standard substance and quantified by the peak area. The invention can effectively detect the content of ammonia in the tobacco water-based glue, and the operation is fast, simple and easy. The gradient elution is used to eliminate the interference of various ions, especially sodium ions, and solve the rapid determination of the ammonia content in the tobacco water-based glue. It fills up the gap in the current determination of tobacco water-based gum ammonia.

Description

一种测定烟用水基胶中氨含量的方法A method for measuring ammonia content in water-based glue for tobacco

技术领域 technical field

本发明属于卷烟加工技术领域,涉及烟用水基胶的理化检验技术,特别是涉及一种测定烟用水基胶中氨含量的方法。 The invention belongs to the technical field of cigarette processing, and relates to a physical and chemical inspection technology for tobacco water-based glue, in particular to a method for measuring ammonia content in tobacco water-based glue.

背景技术 Background technique

烟用水基胶是卷烟生产过程中不可缺少的材料,目前国内卷烟生产中使用的胶黏剂大多是化学合成的水基胶,针对目前烟用水基胶出台的相关检测标准,pH测定是一项重要的指标,有些商家为了使烟用水基胶的pH值达到相应的技术标准,会通入氨气调节其pH值,那么产品中残留的氨不仅会带来不愉快的刺激性气味,还会严重影响卷烟产品的感官质量。因为在卷烟吸食过程中,过量的氨会产生强烈的刺激性,引起吸烟者喉部出现收缩作用,感到呛咳,鼻尖、舌部辛辣难忍,同时与其他含氮类化合物参与了烟气吃味劲头的形成。因此无论是从卷烟吸食安全性还是从感官质量方面考虑,烟用水基胶中氨的残留分析和监控都具有重要的意义。 Tobacco water-based adhesive is an indispensable material in the cigarette production process. At present, most of the adhesives used in domestic cigarette production are chemically synthesized water-based adhesives. According to the relevant testing standards for tobacco water-based adhesives, pH measurement is an important task. An important indicator, in order to make the pH value of the tobacco water-based adhesive meet the corresponding technical standards, some merchants will pass ammonia gas to adjust the pH value, so the residual ammonia in the product will not only bring unpleasant pungent smell, but also seriously Affect the sensory quality of cigarette products. Because in the process of smoking cigarettes, excessive ammonia will produce a strong irritant, causing the smoker's throat to constrict, feel coughing, and the tip of the nose and tongue are unbearably spicy. The formation of flavor energy. Therefore, the analysis and monitoring of ammonia residues in water-based adhesives for tobacco use is of great significance both in terms of cigarette smoking safety and sensory quality.

C.H.Sloan 等用氨电极法测定了卷烟烟气中的氨,该方法前处理复杂,用稀盐酸溶液吸收烟气中的氨然后加入氢氧化钠溶液,蒸馏,再用稀盐酸溶液吸收溢出的氨,然后加入氢氧化钠溶液,进行测定,操作复杂,而且易受环境影响。C.W.Ayers 等用气相色谱法测定了卷烟烟气中的氨,该方法中样品溶液在气相色谱分析前需加强碱进行干燥,样品峰会出现拖尾现象,为克服这点,在进样时额外使用了一种很复杂的by-pass装置,该方法操作冗长,进样复杂,线性范围窄。国内对此方面的研究起步晚,目前主要是有关卷烟主流烟气中氨含量的测定。有关烟用水基胶中氨的测定方法未见报道。 C.H.Sloan et al. used the ammonia electrode method to measure ammonia in cigarette smoke. This method is complicated in pretreatment. Use dilute hydrochloric acid solution to absorb the ammonia in the flue gas, then add sodium hydroxide solution, distill, and then use dilute hydrochloric acid solution to absorb the overflowing ammonia. , and then add sodium hydroxide solution to measure, the operation is complex, and it is easily affected by the environment. C.W.Ayers et al. used gas chromatography to measure ammonia in cigarette smoke. In this method, the sample solution needs to be dried with alkali before gas chromatographic analysis, and the peak of the sample appears tailing phenomenon. To overcome this, an additional A very complex by-pass device was developed. The method is tedious in operation, complicated in sample injection, and narrow in linear range. Domestic research on this aspect started late, and currently it is mainly related to the determination of ammonia content in mainstream smoke of cigarettes. There is no report on the determination method of ammonia in water-based rubber for tobacco.

发明内容 Contents of the invention

本发明的目的在于针对现有技术的不足,提供一种测定烟用水基胶中氨含量的方法,采用离子色谱电导检测法(IC)对烟用水基胶进行直接测定,显著提升测定效率和准确度。 The purpose of the present invention is to address the deficiencies of the prior art, to provide a method for measuring the ammonia content in the tobacco water-based glue, and to directly measure the tobacco water-based glue by ion chromatography conductivity detection (IC), which significantly improves the measurement efficiency and accuracy Spend.

本发明的目的通过以下技术方案予以实现。 The purpose of the present invention is achieved through the following technical solutions.

除非另有说明,本发明所采用的百分数均为重量百分数。 Unless otherwise stated, the percentages used in the present invention are all percentages by weight.

一种测定烟用水基胶中氨含量的方法,包括以下步骤: A method for measuring ammonia content in water-based glue for tobacco use, comprising the following steps:

1、称取待测烟用水基胶样品0.3 g,置于50 mL锥形瓶中; 1. Weigh 0.3 g of the water-based adhesive sample to be tested and place it in a 50 mL conical flask;

2、移取浓度10 mmoL/L的盐酸溶液20 mL,加入到装有待测样品的锥形瓶中,塞上塞子,经150 r/min 振荡10 min,静止; 2. Pipette 20 mL of hydrochloric acid solution with a concentration of 10 mmoL/L, add it to the Erlenmeyer flask containing the sample to be tested, plug the stopper, shake at 150 r/min for 10 min, and stand still;

3、取步骤(2)萃取液10 mL置于离心管中,6500 r/min 离心20 min,取上层清液过0.2 μm 水相滤膜,上离子色谱仪分析; 3. Take 10 mL of the extract from step (2) and put it in a centrifuge tube, centrifuge at 6500 r/min for 20 min, take the supernatant and pass it through a 0.2 μm water phase filter membrane, and analyze it with an ion chromatograph;

4、准备NH4标准工作溶液:称取氨标准溶液,用10 mmoL/L盐酸水溶液定容,然后由10 mmoL/L盐酸水溶液逐级稀释为具有浓度梯度的NH4标准工作溶液;  4. Prepare the NH 4 standard working solution: weigh the ammonia standard solution, dilute it with 10 mmoL/L hydrochloric acid aqueous solution, and then gradually dilute it with a 10 mmoL/L hydrochloric acid aqueous solution to obtain a NH 4 standard working solution with a concentration gradient;

5、将配制好的不同浓度的NH4标准工作溶液进行离子色谱仪分析,以外标法进行定量分析,并以氨的色谱峰面积与其相应的浓度进行回归分析,得到标准曲线,相关系数大于等于0.999,对制备的样品进行测定,测得样品中氨的峰面积,带入标准曲线,求得样品中氨的含量; 5. Analyze the prepared NH4 standard working solutions with different concentrations by ion chromatography, perform quantitative analysis with the external standard method, and perform regression analysis with the chromatographic peak area of ammonia and its corresponding concentration to obtain a standard curve, and the correlation coefficient is greater than or equal to 0.999, the prepared sample is measured, the peak area of ammonia in the sample is measured, and brought into the standard curve to obtain the content of ammonia in the sample;

6、由NH4标准物质保留时间定性,由峰面积定量。 6. Qualitative by retention time of NH 4 standard substance, quantitative by peak area.

其中,所述的离子色谱仪分析条件为:采用CS-12A阳离子交换柱,CG-12A保护柱,CSRS-ULTRA-Ⅱ(4mm)自身再生阳离子抑制器;淋洗液流量:1.2 mL/min,淋洗液由去离子水和浓度为0.05 moL/L甲烷磺酸溶液配制而成,采用梯度淋洗液洗脱;柱温:30℃;检测池温度:35℃;进样量:25 μL;电流:90 mA;所述的梯度淋洗过程为:30%的甲烷磺酸溶液和70%的甲烷磺酸溶液平衡6 min,淋洗液组成为50%的去离子水和50%的甲烷磺酸溶液运行6.1~14.5 min,淋洗液变为30%的甲烷磺酸溶液和70%的甲烷磺酸溶液运行14.5~18 min。 Wherein, the analysis conditions of the ion chromatograph are: adopt CS-12A cation exchange column, CG-12A guard column, CSRS-ULTRA-II (4mm) self-regenerating cation suppressor; eluent flow rate: 1.2 mL/min, The eluent is prepared from deionized water and methanesulfonic acid solution with a concentration of 0.05 moL/L, and is eluted with a gradient eluent; column temperature: 30°C; detection cell temperature: 35°C; injection volume: 25 μL; Current: 90 mA; the gradient elution process is: 30% methanesulfonic acid solution and 70% methanesulfonic acid solution balance for 6 min, and the eluent composition is 50% deionized water and 50% methanesulfonic acid The acid solution runs for 6.1-14.5 minutes, and the eluent becomes 30% methanesulfonic acid solution and 70% methanesulfonic acid solution for 14.5-18 minutes.

步骤4中所述的具有浓度梯度的氨标准工作溶液的具体配制方法为:移取1 mL NH4 +标准溶液,用10 mmoL/L盐酸水溶液定容至100 mL容量瓶中,得到浓度为10 μg/mL的NH4 +一级标准溶液,分别取0.5 mL、1.0 mL、3.0 mL、5.0 mL、10 mL、15 mL、20 mL一级标准溶液,用10 mmoL/L盐酸水溶液定容至100 mL容量瓶中,得到以下浓度的标准序列:0.05 μg/mL、0.1 μg/mL、0.3 μg/mL、0.5 μg/mL、1.0 μg/mL、1.5 μg/mL、2.0 μg/mL。 The specific preparation method of the ammonia standard working solution with a concentration gradient described in step 4 is: pipette 1 mL NH 4 + standard solution, use 10 mmoL/L hydrochloric acid aqueous solution to make up the volume in a 100 mL volumetric flask, and obtain a concentration of 10 μg/mL NH 4 + primary standard solution, take 0.5 mL, 1.0 mL, 3.0 mL, 5.0 mL, 10 mL, 15 mL, 20 mL primary standard solution respectively, and dilute to 100 mL with 10 mmoL/L hydrochloric acid aqueous solution mL volumetric flasks, obtain a standard sequence at the following concentrations: 0.05 μg/mL, 0.1 μg/mL, 0.3 μg/mL, 0.5 μg/mL, 1.0 μg/mL, 1.5 μg/mL, 2.0 μg/mL.

相对于现有技术,本发明具有以下优点: Compared with the prior art, the present invention has the following advantages:

1、本发明首创性地运用离子色谱电导检测法(IC)对烟用水基胶中的氨含量进行精确测定,其操作快速可靠、简便易行,具有测定结果准确、灵敏度高及重复性好的优点,填补了现有技术的空白。 1. The present invention uses ion chromatography conductometric detection (IC) for the first time to accurately measure the ammonia content in the water-based glue for cigarettes. The operation is fast, reliable, simple and easy, and has the advantages of accurate measurement results, high sensitivity and good repeatability The invention has the advantages of filling up the gaps in the prior art.

2、采用浓度为10 mmoL/L的盐酸水溶液作为萃取剂,可有效提高纯化效果和回收率,能有效地使氨从水基胶中萃取出来,因为氨呈碱性,易与酸溶液发生反应而被萃取。 2. Using hydrochloric acid aqueous solution with a concentration of 10 mmoL/L as the extraction agent can effectively improve the purification effect and recovery rate, and can effectively extract ammonia from water-based glue, because ammonia is alkaline and easily reacts with acid solution was extracted.

3、为了有更好的分离度,本发明采用梯度淋洗,梯度淋洗能让主要干扰物质钠离子与氨离子的组分峰分开且无相互干扰,达到定量要求。 3. In order to have a better separation degree, the present invention adopts gradient elution, which can separate the component peaks of the main interfering substance sodium ions and ammonia ions without mutual interference, and meet the quantitative requirements.

4、本发明方法的检出限和定量限 4. Detection limit and quantitative limit of the inventive method

将最低浓度的标准溶液平行测定10次,求其标准偏差,3倍标准偏差作为方法检出限,10倍标准偏差作为定量限。结果为检出限:0.007 μg/g,定量限:0.024 μg/g。 The standard solution with the lowest concentration was measured in parallel 10 times, and its standard deviation was calculated. 3 times the standard deviation was used as the detection limit of the method, and 10 times the standard deviation was used as the limit of quantification. The results were detection limit: 0.007 μg/g, quantification limit: 0.024 μg/g.

5、本发明方法的重复性和加标回收率试验 5. Repeatability and standard addition recovery test of the inventive method

   我们分别做了空白加标和样品加标,然后分别进行样品前处理和离子色谱仪分析,并按照加标量和测定值计算其回收率。结果见表1,由表1可以看出,在3个加标水平上,二甘醇的平均回收率为97.89%。平均相对标准偏差(RSD)为3.14%,说明本方法的回收率较高,重复性好。 We did blank spike and sample spike respectively, and then carried out sample pretreatment and ion chromatography analysis respectively, and calculated the recovery rate according to the spiked amount and the measured value. The results are shown in Table 1. It can be seen from Table 1 that the average recovery of diethylene glycol was 97.89% at the three spiked levels. The average relative standard deviation (RSD) was 3.14%, indicating that the recovery rate of this method is high and the repeatability is good.

表1 氨的回收率和重复性试验(n=5)Table 1 Ammonia recovery and repeatability test (n=5)

Figure 574429DEST_PATH_IMAGE001
Figure 574429DEST_PATH_IMAGE001

    6、本发明氨的前处理重复性试验 6. Repeatability test of pretreatment of ammonia in the present invention

对同一样品不同时间取样,通过上述试样前处理和离子色谱电导检测,计算测定值的相对标准偏差,其结果见表2,说明方法的前处理重复性好。  The same sample was sampled at different times, and the relative standard deviation of the measured value was calculated through the above-mentioned sample pretreatment and ion chromatography conductivity detection. The results are shown in Table 2, which shows that the pretreatment of the method has good repeatability. the

表2 烟用水基胶中氨含量测定的重复性 Table 2 Repeatability of determination of ammonia content in water-based adhesive for tobacco

附图说明 Description of drawings

图1为本发明测定方法的流程图; Fig. 1 is the flowchart of assay method of the present invention;

图2为氨标准工作溶液的色谱图; Fig. 2 is the chromatogram of ammonia standard working solution;

图3为氨的标准曲线图; Fig. 3 is the standard curve figure of ammonia;

图4为烟用水基胶样品中氨的色谱图。 Fig. 4 is a chromatogram of ammonia in a sample of water-based adhesive for tobacco use.

具体实施方式 Detailed ways

下面结合附图和实施例对本发明作进一步的详细说明,但附图和实施例并不是对本发明的限定。 The present invention will be further described in detail below in conjunction with the accompanying drawings and examples, but the accompanying drawings and examples do not limit the present invention.

实施例1Example 1

测定烟用水基胶中氨含量(测定流程如图1所示) Determination of ammonia content in tobacco water-based adhesive (determination process shown in Figure 1)

(1)萃取液的制备:准确称取1.0 g 36%~38%HCl溶液,用18.2Ω去离子水定容至1L,得到10 mmoL/L的盐酸水溶液。 (1) Preparation of extract: Accurately weigh 1.0 g of 36%-38% HCl solution, dilute to 1L with 18.2Ω deionized water, and obtain 10 mmoL/L hydrochloric acid aqueous solution.

    (2)标准工作溶液的制备:氨标准溶液由国家物质中心购得,浓度为:1000 μg/mL,具有浓度梯度的氨标准工作溶液的具体配制方法为:移取1 mL NH4 +标准溶液,用10 mmoL/L盐酸水溶液定容至100 mL容量瓶中,得到浓度为10 μg/mL的NH4 +一级标准溶液,分别取0.5 mL、1.0 mL、3.0 mL、5.0 mL、10 mL、15 mL、20 mL一级标准溶液,用10 mmoL/L盐酸水溶液定容至100 mL容量瓶中,得到以下浓度的标准序列:0.05 μg/mL、0.1 μg/mL、0.3 μg/mL、0.5 μg/mL、1.0 μg/mL、1.5 μg/mL、2.0 μg/mL。得到的标准工作溶液现配现用;氨标准工作溶液色谱图如2所示。                (2) Preparation of the standard working solution: the ammonia standard solution was purchased from the National Material Center, the concentration is: 1000 μg/mL, the specific preparation method of the ammonia standard working solution with a concentration gradient is: pipette 1 mL NH 4 + standard solution , dilute to 100 mL volumetric flask with 10 mmoL/L hydrochloric acid aqueous solution to obtain NH 4 + primary standard solution with a concentration of 10 μg/mL, take 0.5 mL, 1.0 mL, 3.0 mL, 5.0 mL, 10 mL, 15 mL, 20 mL primary standard solution, dilute to 100 mL volumetric flask with 10 mmoL/L hydrochloric acid aqueous solution, and obtain standard series with the following concentrations: 0.05 μg/mL, 0.1 μg/mL, 0.3 μg/mL, 0.5 μg /mL, 1.0 μg/mL, 1.5 μg/mL, 2.0 μg/mL. The obtained standard working solution is prepared and used now; the chromatogram of the ammonia standard working solution is shown in Figure 2.

    (3)样品溶液的制备:准确称取0.3 g烟用水基胶样品,放入50 mL锥形瓶中,用移液管准确加入20 mL 10 mmoL/L 盐酸水溶液,150 r/min 振荡10 min,移取10 mL 于离心管中 6500 r/min 离心20 min,取上层清液过0.2 μm的水相滤膜,上离子色谱仪分析。 (3) Preparation of sample solution: Accurately weigh 0.3 g of tobacco water-based adhesive sample, put it into a 50 mL conical flask, accurately add 20 mL of 10 mmoL/L hydrochloric acid aqueous solution with a pipette, and shake at 150 r/min for 10 min , pipette 10 mL into a centrifuge tube, centrifuge at 6500 r/min for 20 min, take the supernatant and pass it through a 0.2 μm water phase filter membrane, and analyze it with an ion chromatograph.

(4)离子色谱仪分析:分别取标准工作溶液和样品溶液进行离子色谱仪分析,其色谱分析条件为:采用CS-12A阳离子交换柱,CG-12A保护柱,CSRS-ULTRA-Ⅱ(4mm)自身再生阳离子抑制器;淋洗液流量:1.2 mL/min,淋洗液由去离子水和浓度为0.05 moL/L甲烷磺酸,采用梯度淋洗液洗脱;柱温:30℃;检测池温度:35℃;进样量:25 μL;电流:90 mA;所述的梯度淋洗过程为:30%的甲烷磺酸溶液和70%的甲烷磺酸溶液平衡6 min,然后淋洗液组成为50%的去离子水和50%的甲烷磺酸溶液运行6.1~14.5 min,淋洗液变为30%的甲烷磺酸溶液和70%的甲烷磺酸溶液运行14.5~18 min; (4) Ion chromatograph analysis: Take standard working solution and sample solution for ion chromatograph analysis respectively, and the chromatographic analysis conditions are: CS-12A cation exchange column, CG-12A guard column, CSRS-ULTRA-Ⅱ (4mm) Self-regenerating cation suppressor; eluent flow rate: 1.2 mL/min, eluent is composed of deionized water and methanesulfonic acid with a concentration of 0.05 moL/L, and is eluted with gradient eluent; column temperature: 30°C; detection pool Temperature: 35°C; Injection volume: 25 μL; Current: 90 mA; The gradient elution process is: 30% methanesulfonic acid solution and 70% methanesulfonic acid solution are equilibrated for 6 minutes, and then the eluent is composed of Run for 50% deionized water and 50% methanesulfonic acid solution for 6.1 to 14.5 minutes, and change the eluent to 30% methanesulfonic acid solution and 70% methanesulfonic acid solution for 14.5 to 18 minutes;

(5)标准曲线绘制及结果计算:首先以氨组分峰的峰面积对应其相应浓度进行回归分析,得到标准曲线(如图3所示)及回归方程和相关系数,取最低浓度工作溶液,做10次平行试验,计算标准偏差,3倍标准偏差为检出限,10倍标准偏差为定量检测限,结果如表3所示; (5) Standard curve drawing and result calculation: firstly, regression analysis was performed based on the peak area of the ammonia component peak corresponding to its corresponding concentration, and the standard curve (as shown in Figure 3) and regression equation and correlation coefficient were obtained, and the lowest concentration of the working solution was taken. Do 10 parallel experiments, calculate the standard deviation, 3 times of the standard deviation is the detection limit, and 10 times of the standard deviation is the quantitative detection limit, the results are as shown in Table 3;

表3 烟用水基胶中氨的标准曲线和检测限Table 3 Standard curve and detection limit of ammonia in tobacco water-based adhesive

名 称Name 保留时间(min)retention time (min) 回归方程regression equation 相关系数correlation coefficient 检出限(μg/g)Detection limit (μg/g) 定量限(μg/g)Limit of quantitation (μg/g) ammonia 4.834.83 y=6.7625x+0.0022y=6.7625x+0.0022 0.99980.9998 0.0070.007 0.0240.024

然后将测得样品中氨的色谱峰面积带入所绘制的标准曲线,求得样品中氨的含量,计算公式如下: Then the chromatographic peak area that records ammonia in the sample is brought into the standard curve drawn, obtains the content of ammonia in the sample, and calculation formula is as follows:

        X=(C×V×17)/(m×18) X=(C×V×17)/(m×18)

式中:X- 式样中氨的含量,单位为微克/克(μg/g); In the formula: X- content of ammonia in the sample, the unit is microgram/gram (μg/g);

      C- 由标准工作曲线读取的样品中氨的含量,单位为微克/克(μg/g); C- The content of ammonia in the sample read from the standard working curve, in micrograms/gram (μg/g);

      V- 样品所加入萃取液的体积,单位为毫升(mL); V- The volume of the extract added to the sample, in milliliters (mL);

      17- NH3的式量; The formula weight of 17- NH3 ;

      18- NH4+的式量; The formula weight of 18-NH 4+ ;

      m- 式样的质量,单位为克(g); m- the mass of the pattern, in grams (g);

具体结果如表4所示。 The specific results are shown in Table 4.

表4 烟用水基胶中氨含量的检测结果Table 4 Test results of ammonia content in water-based adhesive for tobacco

化合物compound 含 量(μg/g)Content (μg/g) ammonia 78.8578.85

实施例2Example 2

    测定不同品牌烟用水基胶中氨的含量:   Determination of ammonia content in different brands of tobacco water-based adhesives:

    1、样品溶液的制备:准确称取6个品牌的烟用水基胶样品各0.3 g,放入50 mL锥形瓶中,用移液管准确加入20 mL 10 mmoL/L 盐酸水溶液,150 r/min 振荡10 min,移取10 mL 于离心管中 6500 r/min 离心20 min,取上层清液过0.2 μm的水相滤膜,上离子色谱仪分析;样品中氨的色谱图如图4所示。 1. Preparation of sample solution: Accurately weigh 0.3 g of each of the 6 brands of tobacco water-based adhesive samples, put them into a 50 mL conical flask, and accurately add 20 mL of 10 mmoL/L hydrochloric acid aqueous solution with a pipette, 150 r/L min Shake for 10 min, pipette 10 mL into a centrifuge tube, centrifuge at 6500 r/min for 20 min, take the supernatant to pass through a 0.2 μm water phase filter membrane, and analyze it on an ion chromatograph; the chromatogram of ammonia in the sample is shown in Figure 4 Show.

2、采用实施例1的色谱条件分析样品溶液;样品中氨的色谱图如图4所示。 2. Using the chromatographic conditions of Example 1 to analyze the sample solution; the chromatogram of ammonia in the sample is shown in Figure 4.

3、将测得氨的色谱峰面积带入实施例1的标准方程,求得样品中氨的含量,计算方法同实施例1的计算方法,具体结果如表5所示: 3, the chromatographic peak area that records ammonia is brought into the standard equation of embodiment 1, obtains the content of ammonia in the sample, calculation method is with the calculation method of embodiment 1, and concrete result is as shown in table 5:

表5 烟用水基胶中氨含量的检测结果Table 5 Test results of ammonia content in water-based adhesive for tobacco

注:N.D.表示未检出 Note: N.D. means not detected

实施例3Example 3

本实施例对本发明方法的重复性和加标回收率进行验证: The present embodiment verifies the repeatability and standard addition recovery of the inventive method:

分别在样品中加入不同浓度的标准工作溶液,每个样品分别测定3次,测定色谱分析条件同实施例1,根据分析结果计算本方法烟用水基胶中氨的加标回收率及加标后测定的相对标准偏差,结果如表6所示: Add different concentrations of standard working solutions to the samples respectively, measure each sample 3 times, measure the chromatographic analysis conditions with the same embodiment 1, and calculate the recovery rate of ammonia in the water-based glue for tobacco and the concentration after the addition of the standard according to the analysis results. The relative standard deviation of determination, the result is as shown in table 6:

表6加标回收率及相对标准偏差结果Table 6 Standard addition recovery and relative standard deviation results

由表6可知,氨的回收率在94%~101%之间,平均相对标准偏差(RSD)在2.0~5.0之间,说明本发明方法的回收率高,重复性好。 It can be seen from Table 6 that the recovery rate of ammonia is between 94% and 101%, and the average relative standard deviation (RSD) is between 2.0 and 5.0, which shows that the recovery rate of the method of the present invention is high and the repeatability is good.

Claims (2)

1.一种测定烟用水基胶中氨含量的方法,包括以下步骤:1. A method for measuring ammonia content in the water-based adhesive for tobacco, comprising the following steps: (1)称取待测烟用水基胶样品0.3 g,置于50 mL锥形瓶中;(1) Weigh 0.3 g of the water-based adhesive sample to be tested and place it in a 50 mL conical flask; (2)移取浓度10 mmoL/L的盐酸溶液20 mL,加入到装有待测样品的锥形瓶中,塞上塞子,经150 r/min 振荡10 min,静止;(2) Pipette 20 mL of hydrochloric acid solution with a concentration of 10 mmoL/L, add it to the Erlenmeyer flask containing the sample to be tested, plug the stopper, vibrate at 150 r/min for 10 min, and stand still; (3)取步骤(2)萃取液10 mL置于离心管中,6500 r/min 离心20 min,取上层清液过0.2 μm 水相滤膜,上离子色谱仪分析;所述的离子色谱仪分析条件为:采用CS-12A阳离子交换柱,CG-12A保护柱,CSRS-ULTRA-Ⅱ自身再生阳离子抑制器;淋洗液流量:1.2 mL/min,淋洗液由去离子水和浓度为0.05 moL/L甲烷磺酸溶液配制而成,采用梯度淋洗液洗脱;柱温:30℃;检测池温度:35℃;进样量:25μL;电流:90 mA;所述的梯度淋洗过程为:30%的甲烷磺酸溶液和70%的甲烷磺酸溶液平衡6 min,淋洗液组成为50%的去离子水和50%的甲烷磺酸溶液运行6.1~14.5 min,淋洗液变为30%的甲烷磺酸溶液和70%的甲烷磺酸溶液运行14.5~18 min;(3) Take 10 mL of the extract from step (2) and put it in a centrifuge tube, centrifuge at 6500 r/min for 20 min, take the supernatant and pass it through a 0.2 μm water phase filter membrane, and analyze it on an ion chromatograph; The analysis conditions are: CS-12A cation exchange column, CG-12A guard column, CSRS-ULTRA-II self-regenerating cation suppressor; eluent flow rate: 1.2 mL/min, eluent made of deionized water and concentration of 0.05 Prepared with moL/L methanesulfonic acid solution, eluted with gradient eluent; column temperature: 30°C; detection cell temperature: 35°C; sample volume: 25μL; current: 90 mA; the gradient elution process described It is: 30% methanesulfonic acid solution and 70% methanesulfonic acid solution equilibrate for 6 minutes, the eluent composition is 50% deionized water and 50% methanesulfonic acid solution, run for 6.1-14.5 minutes, the eluent becomes Run for 14.5-18 minutes for 30% methanesulfonic acid solution and 70% methanesulfonic acid solution; (4)准备氨标准工作溶液:称取氨标准溶液,用10 mmoL/L盐酸水溶液定容,然后由10 mmoL/L盐酸水溶液逐级稀释为具有浓度梯度的氨标准工作溶液;(4) Prepare the ammonia standard working solution: weigh the ammonia standard solution, dilute it with 10 mmoL/L hydrochloric acid aqueous solution, and then gradually dilute it with 10 mmoL/L hydrochloric acid aqueous solution to obtain the ammonia standard working solution with a concentration gradient; (5)将配制好的不同浓度的氨标准工作溶液进行离子色谱仪分析,以外标法进行定量分析,并以氨的色谱峰面积与其相应的浓度进行回归分析,得到标准曲线,相关系数大于等于0.999,对制备的样品进行测定,测得样品中氨的峰面积,带入标准曲线,求得样品中氨的含量;(5) Analyze the prepared ammonia standard working solutions with different concentrations by ion chromatography, conduct quantitative analysis with external standard method, and perform regression analysis on the chromatographic peak area of ammonia and its corresponding concentration to obtain a standard curve, and the correlation coefficient is greater than or equal to 0.999, the prepared sample is measured, the peak area of ammonia in the sample is measured, and brought into the standard curve to obtain the content of ammonia in the sample; (6)由氨标准物质保留时间定性,由峰面积定量。(6) Qualitative by retention time of ammonia standard substance, quantitative by peak area. 2.根据权利要求1所述的测定方法,其特征在于:步骤(4)中所述的具有浓度梯度的氨标准工作溶液的具体配制方法为:移取1 mL氨标准溶液,用10 mmoL/L盐酸水溶液定容至100 mL容量瓶中,得到浓度为10 μg/mL的氨一级标准溶液,分别取0.5 mL、1.0 mL、3.0 mL、5.0 mL、10 mL、15 mL、20 mL一级标准溶液,用10 mmoL/L盐酸水溶液定容至100 mL容量瓶中,得到以下浓度的标准序列:0.05 μg/mL、0.1 μg/mL、0.3 μg/mL、0.5 μg/mL、1.0 μg/mL、1.5 μg/mL、2.0 μg/mL。2. The assay method according to claim 1, characterized in that: the specific preparation method of the ammonia standard working solution with a concentration gradient described in step (4) is: pipette 1 mL of ammonia standard solution, and use 10 mmoL/ Dilute 1 L hydrochloric acid aqueous solution to a 100 mL volumetric flask to obtain a primary standard solution of ammonia with a concentration of 10 μg/mL, and take 0.5 mL, 1.0 mL, 3.0 mL, 5.0 mL, 10 mL, 15 mL, and 20 mL of the primary standard solution respectively. Standard solution, dilute to 100 mL volumetric flask with 10 mmoL/L hydrochloric acid aqueous solution, and obtain the standard sequence of the following concentrations: 0.05 μg/mL, 0.1 μg/mL, 0.3 μg/mL, 0.5 μg/mL, 1.0 μg/mL , 1.5 μg/mL, 2.0 μg/mL.
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